• 한국환경복원기술학회지
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• 제12권2호
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• pp.83-94
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• 2009

Environmental pollution becomes a serious problem in urban areas. Moreover, densely constructed strictures can be problematic to cities due to the rising temperature they cause as well as the increasing accumulation of air pollutants they generate by interrupting airflow. In order to improve residential amenity, it is necessary to improve the thermal environment by preserving wind corridors. To do so requires consideration to important aspects such as building arrangement, scale, vegetation, and land cover, which all have an effect on wind corridors. In this study, a typical arrangement-complex, which is the primary form of housing in Korea, was selected as a case ENVI-met. As a result of empirical analysis, the optimal apartment-complex arrangement that is most suitable for mitigating urban heat-islands phenomenon was determined, The outcome of this study can be utilized as a planning technique for apartment-complex construction in consideration to type of buildings, scale of buildings, and land cover.

• 한국환경생태학회지
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• 제24권5호
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• pp.575-581
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• 2010

본 연구는 도시생태계 보전 및 복원을 위한 기반으로 활용되고 있는 비오톱조사자료의 현장조사 정확도를 검증하고자 하였다. 이를 위해 서울시 관악구 산림지역을 대상으로 2000년과 2005년의 비오톱 현장조사 결과를 바탕으로 인공위성영상에서 확인가능한 상록침엽수림을 추출한 후 두 현장조사결과에 기초하여 현장조사의 정확성을 검증하였다. 분석결과 현장조사에 의한 세부 현존식생의 면적비율은 시기와 조사자의 차이에도 약 92%의 높은 유사도를 보였으나, 두 조사에서 동일한 식생유형이 지리공간상 일치하는 지역은 약 60%에 불과하였다. 인공위성영상에서 추출한 상록침엽수의 위치 분석 결과 2000년 조사와는 69.4%, 2005년과는 80.0%가 일치하는 것으로 분석되었는데, 인공위성 영상 판독오류를 감안했을 때 비교적 높은 정확도를 보이고 있었다. 지금까지 비오톱조사시 현장조사에 의한 식생구분 에 대한 정확성 검증이 이루어지지 않고 수행되어 왔으나, 향후 자료의 갱신이나 신규 사업에 있어서는 정확도 검증이 무엇보다 중요하며 이에 대한 구체적 기준마련이 필요하다고 판단된다.

• 한국환경복원기술학회지
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• 제2권1호
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• pp.48-57
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• 1999

This study was aimed to establish biotop unit of the mixed rural city for the method and process of the biotop mapping system. Survey site was Maejuri of Seunghwan(158ha), Gisanri of Mokchon(132ha) and Namkwanri, Pungsemeon(214ha). So the main process was divided by 4 schemes such as Biosphere, Geosphere, Antrosphere and Evaluation. Also the GIS(geographic information system) was used to make the database of the biotop and biotop complex, analyze the cross-combinations and analyze the characters of the biotop. Biotop mapping system had 5 steps which were proceeded with research goals, constructing the spatial database and attribute database, classifying the 3 types of biotop such as tree/shrub biotop, grass biotop and wetland biotop, cross-analyzing 3 biotop types with land use, habitat characters, relief characters and danger/disturbance elements and evaluating the 3 types of biotop. The results of applicating the biotop mapping system on the research site as followings : The distributions of the land uses in Maejuri, Seunghwan eup in Chonan city were recorded by forest(29.8%), orchard(14.1%) and landscaping around building site(9.0%). Gisanri, Mokchonmeon were composed of forest(64.5%), farm(12.8%) and Namkwanri, Pungsemeon were concentrated rice field(39.6%), dwell district(22.4%). The Tree/Shrub biotop type was reclassed by the forest type, natural and artificial decidous type with natural coniferous. The Grass biotop type was reclassed by the wild grassland type, garden type and peddy field with wild grassland. The distributions of the wet land were pointed high at the wet land type with reed marsh and edge vegetation around wet land in reservoir and river. The evaluation of the mapped bitopes was completed to the following aspect, "amenity" and "environmental education". A high value of 7.13%(1 class) was shown Maejuri, Seunghwan eup. The regions which were studied synthetically are divided to three parts ; the area where have nature and art mixed(Seunghwan), the area which is more artificial because people inhabit there for a long time(Pungsemeon) and the area that ecological environment is threatened by development pressure(Mokchonmeon). Therefore, ecological restoration plan which depends on specific property of the regions should be established. Also the interdisplinary researches were needed to develop the BMS(Biotop Mapping System) in Korea because of the differences with Germany, England's ecological habitat conditions.

• 한국산림과학회지
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• 제104권2호
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• pp.206-212
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• 2015

이 연구는 우리나라의 도로비탈면에 주고 적용하고 있는 돌망태공법의 특성을 조사, 분석하고 경관선호도를 분석하였다. 임도 및 도로비탈면에 시공한 97개소의 돌망태를 대상으로 조사한 결과, 10가지 유형으로 분석되었다. 비탈면 경사도에 따른 돌망태 시공지를 분석한 결과, 비탈면 경사 10% 이하지역에서는 돌망태가 30개소(31%), 11~30%의 경사에서는 31개소(32%), 31~50%의 경사에서는 20개소(21%), 51~80%에서는 16개소(16%)로 비탈면의 경사가 낮을수록 돌망태를 많이 시공하는 것으로 분석되었다. 총조사지 중 돌망태에 식생이 피복되지 않은 개소수는 34개소(35%)로 나타났으며, 1~30% 정도의 식생피복을 나타낸 개소수는 52개소(54%)로 가장 높게 나타났다. 설문조사를 통한 경관분석 결과 일반인집단은 비탈면에 돌망태를 시공할 때 식생으로 피복되는 것이 경관을 좋게 하는 요인으로 의식하고 있었다. 전문가집단은 비탈면에 돌망태만 처리한 경관을 가장 선호하였으며, 그 다음으로는 비탈면에 돌망태를 시공할 때 식생으로 피복되는 것이 경관을 좋게 하는 요인으로 판단하고 있는 것으로 분석되었다.

• 한국환경생태학회지
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• 제26권2호
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• pp.219-232
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• 2012

본 연구는 인왕산의 과거 기록자료 및 문화경관지역에 나타난 소나무림의 분포 특성을 파악하여 소나무림 경관복원을 위한 관리방안을 수립하는데 목적이 있다. 인왕산의 과거 소나무림은 정선, 장시흥, 강희언의 산수화에서 잘 표현되어 있는데, 주로 동사면 능선부의 암반 주변을 표현하고 있었다. 인왕산 사진자료는 1800년대 말부터 기록되어 있는데 소나무림은 주로 서측 사면 저지대와 능선부에 분포하고 있었다. 인왕산의 문화유적 주변과 암반 주변 경관을 분석한 결과 대부분 소나무림이 우점하고 있었다. 인왕산의 과거 소나무림 경관을 형성하고 있는 지역을 대상으로 현존식생을 분석한 결과 소나무림을 유지하고 있는 지역은 51.87%, 인공림 변화한 지역이 25.80%이었다. 산림 저지대 소나무림은 대부분 시가화지역(10.16%)으로 변화되었다. 인왕산 소나무림 경관 복원을 위한 관리유형구분은 보전관리, 소나무복원관리, 유지관리로 설정하였다. 보전관리는 소나무림 분포지와 암반 분포지역으로 설정하였고 소나무 복원관리는 능선부의 자생종 낙엽활엽수 분포지, 외래종 식생 분포지와 산림 내 훼손지역으로 설정하였다. 유지관리지역은 인왕산 저지대 시가화지역과 인왕산 정상부의 군부대 입지지역으로 설정하였다.

• 한국조경학회지
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• 제27권2호
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• pp.51-57
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• 1999

Planting methods of seeding, seed net, sprig net and sprigging were evaluated for influence on the covering rate and the growth of Phragmites spp. The results were as follows. 1. Covering rate was high within 4 months when propagated by sprig net, seeding and sprigging but became same within 5 months afterwards regardless of Planting methods. 2. Growth of leaf height and width was high on vegetative types of Planting methods such as sprig net and sprigging when compared with on seed types of Planting methods such as seeding and seed net. 3. Sprig net showed good covering rate and growth than sprigging when compared within vegetative types of planting. 4. In this study, sprig net was figured out as the best type of Planting methods than any other types of Planting methods for the restoration of a shore vegetation in a urban stream.

• 한국환경복원기술학회지
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• 제3권3호
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• pp.81-99
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• 2000

The shelterbelts are very important to conserve and protect the sandy land, vegetation coverage, farmland, livestock and human life in the desertified land. The shelterbelts are constructed by the several row-plantings of high-adaptable species in the desertified land. The shelterbelts have various kind of type, and there are shelterbelts for conservation of farmland in dry the region, the protective shelterbelts (windbreaks for blowing-sand, artificial sanddune fixation by revegetation, and construction of farmland shelterbelts to protect farmland and pasture from wind erosion, etc.) in the semi-dry steppe, shelterbelts around the villages and oasis for sanddune fixation, shelterbelts for protection of railroads, and so on. The shelterbelts consist of main she1terbelts and minor shelterbelts. The main shelterbelts were constructed by being perpendicular to main wind direction, and the minor shelterbelts were constructed by being perpendicular to the main shelterbelts. Generally, the width of shelterbelts is 8~20m, and the number of row-planting is 4~10. The grid sizes of shelterbelts networks are $400{\times}400m$, $300{\times}500m$, $100{\times}200m$, and so on, and there are ventilation type and closing type in the type of shelterbelt. The width, number of row-planting, grid size and type of shelterbelt are selected by the local characteristics. The effects of shelterbelts are mainly the climate improvement and mitigation, such as prevention of occurrence of strong wind, cold wind and blowing-sand. And, the other effects of shelterbelts are effect of reforestation, increase of agricultural productions, establishment of greenbelts and green forests, construction of landscape-eco shelterbelts, improvement of life environment of local villages, supply of fuel wood and agricultural wood, land amelioration, effect of revegetation and restoration of desertified land, and so on. The kinds of the tree species mainly used for the construction of shelterbelts have differences between regions, but main species are Populus euphratica, Populus simonii, Populus bolleana, Populus tomentosa, Salix flavida, Salix mongolica, Tamarix chinensis, Hedysarum scoparium, and so on.

• 한국조경학회지
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• 제51권3호
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• pp.1-20
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• 2023

본 연구는 둔촌동 생태·경관보전지역을 대상으로 습지 복원 전·후 생물다양성 변화를 모니터링하고, 주변 도시개발 변화에 맞는 습지 관리방안을 제시하고자 하였다. 이를 위해 대표 생물종을 정밀조사하고, 보전지역 및 주변 지역에서 발생하는 생태계 위협요인을 파악·분석하였다. 둔촌동 습지 주변 지역은 과거 산림과 논이었던 지역에 대규모 아파트단지가 조성되고, 일부 배후 산림은 남아있었다. 식물상 변화를 살펴보면, 복원 전 2000년에는 총 193종류이었다가 복원 후 2004년부터 2006년까지 종수가 줄었다가 2019년 현재 총 149종류로 다시 증가하였다. 복원 전·후 출현종을 비교한 결과, 숲 속 습한 습지지역에서 생육하는 왕비늘사초(Carex maximowiczii), 삿갓사초(Carex dispalata)와 습지 내 얕은 물이 유지되는 지역에서 생육하는 올챙이고랭이(Schoenoplectiella juncoides), 큰고랭이(Schoenoplectus tabernaemontani) 등 사초과 초본이 증가하였다. 습지 식생유형별 면적비율 변화를 분석한 결과 복원 이후 습지자생초본이 가장 높은 비율로 세력을 형성하였다. 습지자생초본의 세력 변화는 26.6%(2000) → 44.6%(2002) → 49.0%(2005) → 53.3%(2007) → 28.7%(2010) → 37.3%(2019)로 증가세를 보이다 2010년에 크게 감소 후 점차 확대되고 있다. 2010년 이후 변화는 습지 내 개방수면 확보와 담수지 내 유기물 제거를 위한 전면적인 식생관리가 원인인 것으로 판단된다. 습지자생목본은 복원 후 오리나무(Alnus japonica) 치수가 출현하여 세력을 1.6%(2005) → 6.3%(2007) → 14.8%(2010) → 21.9%(2019)로 계속 확대되고 있었다. 양서류는 2000년부터 2019년까지 모니터링 결과 도롱뇽(Hynobius leechii), 두꺼비(Bufo gargarizans), 맹꽁이(Kaloula borealis), 큰산개구리(Rana uenoi) 등 총 9종이다. 둔촌동 습지의 양서류는 귀화식물 및 자생식물 관리와 담수지 개방수면 확보를 통해 두꺼비, 도롱뇽, 큰산개구리 등 산림을 기반으로 하며 습지에서 서식하는 양서류가 증가한 것으로 판단된다. 야생조류 종다양도 지수는 복원 전 종다양도 지수는 2000년 0.9922, 복원 후 종다양도 지수는 2005년 1.2449, 2010년 1.2467, 2019년 2.2631로 복원 후 수치가 증가하였다. 둔촌동 생태·경관보전지역의 생태계 보전 관리는 둔촌주공 아파트 재건축 공사 영향 최소화, 습지 인접 무분별한 접근로 정비 및 습지 주 진입부 입구 정비를 제시하였다. 생태계 복원 관리에서는 공사 펜스 철거 시 체계적인 생태 복원 및 완충식재를 제시하였다.

• 한국환경복원기술학회지
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• 제14권6호
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• pp.57-69
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• 2011

The present paper deals with a research of life form and vegetation of the plants extant in the habitat of endangered Parnassius bremeri in Uiseong, Gyeongsangbuk-do with a view to restore their habitat and create substitute habitats. The research found that there are a total of 130 vascular plants including 47 families, 96 genera, 113 species, 1 subspecies and 16 varieties. In terms of their life form, hemicryptophytes (H) is the majority of dormancy form with 41 species or 31.54%, while $R_5$ is majority of radicoid form with 72 species or 55.38%, gravitational disseminule form ($D_4$) is majority among the disseminule forms with 68 species or 52.31% and erect type (e) is majority of growth form with 57 species or 43.85%. Major constituents of the habitat are Sedum kamtschaticum, Selaginella tamariscina, Orostachys japonica, Arundinella hirta, Cymbopogon tortilis var. goeringii, Themeda triandra var. japonica, Carex humilis, Indigofera kirilowii, Imperata cylindrica var. koenigii, Festuca ovina, Artemisia capillaris, etc., all of species which are in the initial stage of succession and show simultaneously features characteristic of vegetation on the rock. In the habitat 1. Sedum kamtschaticum- Selaginella tamariscina community and Pinus densiflora community are distributed whereas, in the habitat 2. Sedum kamtschaticum-Selaginella tamariscina community, Sedum kamtschaticum-Carex humilis community, Sedum kamtschaticum-Cymbopogon tortilis var. goeringii community and Sedum kamtschaticum-Imperata cylindrica var. koenigii community are growing and in the habitat 3. Sedum kamtschaticum-Selaginella tamariscina community, Selaginella tamariscina community, Sedum kamtschaticum-Indigofera kirilowii community and Quercus acutissima community are seen distributed there, too. Typical of food plants growing in the habitat is Sedum kamtschaticum, found mostly in the rocky area and its surroundings. Absorption plants are those that usually bloom in the season when imagoes emerge. From the research, it becomes evident that the blooming season of Sedum kamtschaticum, obviously a food plant, corresponds exactly to the emergence timing of imagoes. Cirsium japonicum var. ussuriense, Rosa multiflora, Erigeron annuus, Spiraea prunifolia var. simpliciflora are found to belong to these plants.

• The Korean Journal of Ecology
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• 제24권2호
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• pp.101-109
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• 2001

We created an environmental forest on the basis of ecological design around the incineration plant of Jindo Engineering and Construction Co., Ltd., which is located in Jeongwang-dong, Siheung-si, Kyunggi-do. To get ecological information of this site, physico-chemical properties of soil on salt marsh, which is located close to the syudy site and of forest soil transported from other sites for ecological restoration were analyzed. Texture of salt marsh and transported soils were loam and sandy loam, respectively. pH, organic matter, T-N, available P, and exchangeable K and Na contents of salt marsh and transported forest soils were 6.7 and 5.4, 4.1 and 0.4%, 1.0 and 0.3mg/g, 46.7 and 6.8ppm, 521 and 207ppm, and 3.8 and 0.5mg/g, respectively. Introduced plants were selected among the dominant species of forests and the species composing the potential natural vegetation around the present study site. Those plants were selected again by considering the tolerances to air pollution and to salt, and their availability. Selected trees were Pinus thunbergii, Sophora japonica, Celtis sinensis, Quercus aliena, Q. serrata, Q. dentata, and Q. acutissima. Selected sub-trees were Albizzia julibrissin, Koelreuteria poniculata, and Styrax japonica and shrubs were Rhododendron yedoense var. poukhanense, R. mucronulatum, Callicarpa japonica, Euonymus alatus, E. japonica, and R. schlippenbachii. On the other hand, introduction of herbs was not considered except for Liriope platyphylla, which was ornamentally planted in one site. Planting bed of mound type was adopted to provide the fine drainage system. Mound was designed to furnish litter, A, B, and C layers simuating the profile of forest soil. Slope of mound was mulched by rice straw of 2cm in thickness to prevent for sliding of litter and soil in cases of strong wind or heavy rain. Height of mound was designed to secure more than 1 m by combining A and B layers. Narrow zones, in which mound with stable slope degree cannot be prepared, was designed to equip the standard soil depth with the introduction of stone for supporting. On the other hand, plants with shallow root system were arranged in some zones, in which satisfactory soil depth cannot be ensured. Plants were arranged in the order of tree, sub-tree, and shrub from center to edge on the mound to make a mature forest of a dome shape in the future. Dispersion of plants was designed to be random pattern rather than clumped one. Problems on creation of the environmental forest by such ecological design were found to be management or inspection by non-specialized project operators and inspecting officers, and regulations for construction without ecological background. Alternative plans to solve such problems were suggested.